Comparison of matrix-effect corrections for ordinary and uncertainty weighted linear regressions and determination of major element mean concentrations and total uncertainties of sixty-two international geochemical reference materials from wavelength-dispersive X-ray fluorescence spectrometry☆
Graphical abstract
Introduction
Modern analytical techniques are based on the calibration of instrumental response as a function of elemental concentrations. This calibration consists of fitting a straight-line relationship between these two (concentration x-axis and response y-axis) variables [[1], [2], [3], [4], [5], [6]]. A straight-line fit can be achieved either from the conventional statistically less appropriate or even erroneous ordinary least-squares linear regression (OLR) model or from the modern statistically coherent uncertainty-based weighted least-squares linear regression (UWLR) model [6,7].
In the XRF technique, it is mandatory to correct for the matrix effects (absorption, enhancement, and scattering) before determining the final concentrations [[8], [9], [10], [11], [12], [13], [14], [15]]. These effects can be handled through influence coefficients, which can be divided into three basic types [8]: (i) Regression or Empirical model, which has little connection with the XRF theory but allows the determination of influence coefficients by regression analysis of the data sets obtained from reference materials; (ii) Fundamental Parameter model [9], being a totally theoretical approach, requires starting with concentrations and then calculating the intensities; and (iii) Fundamental Algorithm model, based on some simplification of the Fundamental Parameter method, allows concentrations to be calculated from XRF intensities. The weaknesses of the Fundamental Parameter method were pointed out by Rousseau [8], who advocated for the Fundamental Algorithm model [10,11] to be adopted. The Empirical or Regression model were considered less useful [8]. However, the statistically correct weighted least-squares linear regression (WLR) models have not been evaluated in any of the XRF reviews. Therefore, the inference about less usefulness of the regression procedures may not be strictly valid.
In a more recent review, Rousseau [12] evaluated the Lachance–Traill [14] and Claisse–Quintin models [15] as well as the empirical influence coefficients. Rousseau [12] concluded that the empirical method is most suited for use with the Lachance–Traill [14] algorithm and all other proposed algorithms, such as Rasberry and Heinrich [16] or Lucas-Tooth and Pyne [17], etc., are not recommended because of their extremely limited application range or lack of accuracy. These other algorithms, therefore, are not likely to be useful in geochemistry, because the elemental concentrations may vary widely from 0 to 100%, e.g., SiO2, and, consequently, the other compositional variables will also vary widely [6]. Nevertheless, it may be useful to apply the theoretical Fundamental Parameter method [10,11] under the Claisse–Quintin model [15] and compare it with the empirical model (Lachance–Traill [14] algorithm), along with the OLR and UWLR methodologies. However, for the theoretical model, pure single element materials are required, which are not available to us for the geochemical analysis of major elements or oxides. Rousseau [11] presented a semi-theoretical method, in which the geochemical elements (but not oxides) could be successfully analysed. However, even if successful, the hypothetical example of the major elements presented by Rousseau [11] might not be useful in geochemistry, because oxygen, constituting a large component in all rock and mineral matrices, cannot be easily determined. The presence of oxygen was not even mentioned in the hypothetical examples [11], because all elements, without oxygen, were assumed to sum up to 100%. One may argue that oxygen can be added later to the respective elements as their oxides; however, the conversion of Fe becomes difficult or approximate because of its two oxidation states (FeO and Fe2O3) whose proportion is not known a priori. Nevertheless, an option will be to assume all Fe presented as the one or the other oxide. Therefore, the application, evaluation and comparison of a theoretical method with empirical models for the major element determinations in complex rock and mineral matrices should await the availability of all 10 pure elements or components and the theoretical coefficients.
Rousseau [12] explained that the empirical influence coefficients are derived from the best possible fit between the measured intensities and concentrations of a given set of “proper” reference materials. With the increase of the number (m) of analytes, large number of reference materials (at least, 2m + 1) would be necessary. The other basic requirement is that the preparation of the reference materials and the “unknown” samples should be the same and reproducible. There are other basic requirements for the empirical method [12], which can be better fulfilled by the WLR or UWLR than the OLR model [6]. An advantage of the empirical coefficients is that they must be calculated only once, so long as the sample preparation and instrumental conditions are maintained the same. There is no need to resort to complex theory for concentration calculations [12].
In this paper, therefore, we deal with the empirical approach. For the regression models, recently, the two variants (OLR and UWLR) were compared for the calibration of an XRF spectrometer and it was inferred that the UWLR provided more reliable results [18]. It has been argued that the OLR model is statistically inappropriate, because several assumptions are violated [[2], [3], [4], [5], [6], [7]]. The situation is even worse for the XRF method of rock analysis [6]. Unfortunately, the OLR is the only regression model that has been used in the XRF calibrations, except the recent work by [18].
The LaChance–Traill algorithm [14] is the recommended algorithm for empirical coefficients [12]. Although the authors [18] applied both regressions (OLR and UWLR), they used the same matrix effect correction algorithm for both these regressions. To the best of our knowledge, the matrix-correction equations, specifically for the UWLR model [18], have not yet been reported, nor are their implications deduced for the OLR and UWLR models. We also present a comparison of corrections involving 11 α (a conventional number of alpha corrections or empirical coefficients, i.e., a conventional approach in XRF work) and 26 α (a new approach involving large number of alpha corrections) in the matrix solution for the determination of 10 major elements in geological materials. This was facilitated from an unusually large number of calibrators. It is quite possible that such large number (62) of reference materials may have been used earlier (e.g., by Lezzerini et al. [19]) but the newer more reliable (lesser uncertainties, with narrower confidence limits of the mean) concentrations were never derived nor used before in any research, except [18]. Further, the UWLR model [18] was also not used by anyone, including [19].
Recently, Panchuk et al. [20] presented a review on the chemometric methods applied to the XRF data, in which they pointed out the use different regression models, such as partial least-squares regression and several multivariate techniques. All these techniques make use of the data (mean values or most frequently single measurements), without taking in account both the central tendency and dispersion parameters of experimental data. Therefore, all these methods can be grouped under the heading of OLR models [[2], [3], [4], [5], [6], [7]]. The use of WLR [[2], [3], [4], [5]] or UWLR models [6,7] was not even mentioned in this recent review.
Therefore, we compare two different matrix-effect correction algorithms based on the two types of regressions and propose a new UWLR calibration from 62 geochemical reference materials (GRMs) involving 26 α. We also use the same GRMs as unknowns to determine the 10 major element concentrations and their total uncertainties. The quality of these results was thus evaluated in terms of the known concentrations of the GRMs. Besides showing the superiority of the UWLR model, the innovation of our work lies with the possibility of carrying out matrix-effect corrections for this new statistical model and estimating individually the total uncertainty values, along with the mean concentrations for unknown samples, for which 4 additional GRMs, independent of the calibration procedure, were used as unknowns.
Section snippets
Sample preparation
Multiple pressed powder pellets were prepared for most GRMs used in this study. An appropriate amount of each GRM was dried overnight in an oven at about 105 °C. For each pellet, accurately weighed 3.5000 (±0.0003) g of moisture-free GRMs were thoroughly mixed with accurately weighed 3.0000 (±0.0003) g pure N,N′-Ethylenebis (molecular weight 168.19; (H2C=CHCONHCH2-)2; technical grade ≥ 90%) beads, <840 μm as wax (Sigma-Aldrich) stored in a desiccator. Pressed powder pellets were prepared at 20
Regression equations for the calibration
Conventionally, in XRF spectrometry the concentration-response calibration curves are established from the concentration-intensity (C-I) least-squares linear regressions [1,[4], [5], [6], [7],18,46]. The OLR model does not consider the uncertainties in x and y variables and assigns equal weights to all calibrators; the general calibration equation is as follows [[4], [5], [6], [7],18] (where the subscript O stands for the OLR model):
From the regression of the C-I data (Table
Measurement of concentrations and related total uncertainties of GRMs treated as unknown samples
We also document the results of the analysis of the major elements in all GRMs, each of them treated as unknown (Table 2). In order to compare these UWLR results (Table 2) with the expected GRM concentrations (Table S1 (Appendix)), we derived the respective regression equations (Table 3), instead of presenting individual graphs for each element. All elements showed statistically significant linear correlations with a very low probability of no correlation (Pc(r; n)ʷ < 0.0005; Table 3). Table 3
Computer program MECUX
An online computer program MECUX is available for interested users. A novel aspect of this program is that total 99% uncertainty can be calculated for individual datum in a given sample (treated as unknown; Table 2, Table 4, Table 5). This program should serve as a guideline for calibrations when the user is interested in estimating total analytical errors or uncertainties. The use of these advancements in geochemistry has already been documented [60].
Conclusions
We have developed and evaluated, for the first time, matrix-correction equations for both regressions (the statistically deficient OLR and coherent or correct UWLR). A large number of GRMs (62), with newer more reliable concentrations, have been used for the first time and 26 α have been incorporated in the matrix-effect corrections. The final r values varied from 0.9973 to 0.9999 for the UWLR model, which were significantly higher than those for the OLR model (0.9799 to 0.9994). This
Declaration of Competing Interest
There are no conflicts to declare.
Acknowledgements
This work was supported through Newton Advanced Fellowship Award [grant NA160116] of the Royal Society, U.K. to the last author (SKV). We are grateful to the Nanoscience and Nanotechnology National Research Laboratory (LINAN), Carbon Nanostructures and two-dimensional Systems Laboratory at IPICYT. Our sincere thanks go to Dr. Emilio Muñoz-Sandoval for providing access to the required facilities, to Tech. Beatriz Adriana Rivera-Escoto for initial guidance in the use of the XRF equipment, and to
References (60)
Weighted least squares evaluation of slope from data having errors in both axes
Trends Anal. Chem.
(1990)Corrections for matrix effects in x-ray fluorescence analysis—a tutorial
Spectrochim. Acta Part B
(2006)- et al.
Application of chemometric methods to XRF-data - a tutorial review
Anal. Chim. Acta
(2018) Some considerations on the definition of the limit of detection in X-ray fluorescence spectrometry
Spectrochim. Acta Part B
(1997)- et al.
Evaluation of the odd-even effect in limits of detection for electron microprobe analysis of natural minerals
Anal. Chim. Acta
(2009) - et al.
Statistics and Chemometrics for Analytical Chemistry
(2010) - et al.
Weighted least-squares approach to calculating limits of detection and quantification by modeling variability as a function of concentration
Anal. Chem.
(1997) - et al.
Applied Regression Analysis
(1998) - et al.
Fitting straight lines with replicated observations by linear regression: part II. Testing for homogeneity of variances
Crit. Rev. Anal. Chem.
(2004) Road from Geochemistry to Geochemometrics
(2020)
Geochemometrics
Rev. Mex. Cienc. Geol.
Concept of the influence coefficient
Rigaku J.
Calculation methods for fluorescent x-ray spectrometry. Empirical coefficients versus fundamental parameters
Anal. Chem.
Fundamental algorithm between concentration and intensity in XRF analysis 1—theory
X-Ray Spectrom.
Fundamental algorithm between concentration and intensity in XRF analysis 2—practical application
X-Ray Spectrom.
Debate on some algorithms relating concentration to intensity in XRF spectrometry
Rigaku J.
A practical solution to the matrix problem in X ray analysis
Can. J. Spectrosc.
Generalization of the lachance–traill method for the correction of the matrix effect in X-ray fluorescence analysis
Can. J. Spectrosc.
Calibration for interelement effects in X-ray fluorescence analysis
Anal. Chem.
The accurate determination of major constituents by X-ray fluorescent analysis in the presence of large interelement effects
Adv. X-ray Anal.
Statistically coherent calibration of X-ray fluorescence spectrometry for major elements in rocks and minerals
J. Spectrosc.
Reproducibility, precision and trueness of X-ray fluorescence data for mineralogical and/or petrographic purposes
Atti Soc. Tosc. Sci. Nat., A
1987 compilation report on ailsa craig granite AC-E with the participation of 128 GIT-IWG laboratories
Geostand. Newslett.
Report (1980) on three GIT-IWG rock reference samples: anorthosite from Greenland, AN-G; basalte d' Essey-la-Côte, BE-N; granite de Beauvoir, MA-N
Geostand. Newslett.
1987 compilation of elemental concentration data for USGS BHVO-1, MAG-1, QLO-1, RGM-1, SCo-1, SDC-1, SGR-1, and STM-1
Geostand. Newslett.
Report (1967-1981) on four ANRT rock reference samples: diorite DR-N, serpentine UB-N, bauxite BX-N, disthene DT-N
Geostand. Newslett.
1987 compilation of elemental concentration data for USGS BIR-1, DNC-1 and W-2
Geostand. Newslett.
FeR-1, FeR-2, FeR-3 and FeR-4 four canadian iron-formation samples prepared for use as reference materials
Geol. Surv. Can.
Report (1973-1984) in two ANRT geochemical reference samples: granite GS-N and potash feldspar FK-N
Geostand. Newslett.
1988 compilation of elemental concentration data for USGS geochemical exploration reference materials GXR-1 to GXR-6
Geostand. Newslett.
Cited by (11)
A statistically coherent robust multidimensional classification scheme for water
2021, Science of the Total EnvironmentCitation Excerpt :This should be done especially for the “Analytical errors or uncertainties” concept, irrespective of the basic or combined basic and hybrid water nomenclature. Analytical errors or uncertainties on individual geochemical data are seldom if ever reported although, as recently documented by Verma et al. (2019), it is entirely feasible to do so. Thus, the reports of water analysis seldom, if ever, include analytical errors on individual measurements.
New discriminant-function-based multidimensional discrimination of mid-ocean ridge and oceanic plateau
2020, Geoscience FrontiersCitation Excerpt :For uncertainty propagation, we used the examples of the centroids of the MOR (1126 samples) and OP (1732 samples) as representative of the respective chemical compositions (Item No. 8 in Table 1). Because the total analytical uncertainties are not generally available for individual data as recently pointed out (Verma et al., 2018, 2019; Torres-Sánchez et al., 2019; Verma, 2020), we calculated, for illustration purposes, the 99% uncertainty values for the samples of the database used for the ilrMT model and assigned them to each respective centroid concentration values. These two Excel files (data summarized in Table 2) were processed in the Robustness module of MOPOPdisc (Fig. S3).
Comprehensive multidimensional tectonomagmatic discrimination from log-ratio transformed major and trace elements
2020, LithosCitation Excerpt :In case of controversial indications, the ilrMTd inference should be considered more reliable than the ilrMd model, unless there were some serious analytical problems with the determination of trace elements. Unfortunately, at present, it is seldom, if ever, possible to detect the analytical problems, although it would be so, in future, when most authors start reporting total uncertainties on individual data as illustrated recently by Verma et al. (2018, 2019) and Torres-Sánchez et al. (2019). The locations of the sampling sites for all 13 application cases are shown schematically in Fig. 1.
Petrogenetic and tectonic implications of Oligocene−Miocene volcanic rocks from the Sierra de San Miguelito complex, central Mexico
2019, Journal of South American Earth SciencesCitation Excerpt :Major element for 23 samples were determined by a wavelength dispersive X–ray fluorescence (WD-XRF) spectrometer Rigaku ZSX Primus II at Institute of Scientific and Technological Research of San Luis Potosi, IPICYT (San Luis Potosí, Mexico). The analytical procedures, accuracy, and precision were given by Verma et al. (2018, 2019). The computer program MECUX is available for online use at http://tlaloc.ier.unam.mx.
Petrogenesis and geodynamic implications of Oligocene A-type granite in the Guadalcazar area, San Luis Potosi, central Mexico
2022, Journal of Iberian Geology
- ☆
Selected Paper from the Colloquium Spectroscopicum Internationale XLI & I Latin American Meeting on Laser Induced Breakdown Spectroscopy (CSI XLI - I LAMLIBS) held in Mexico City, Mexico, June 9–14, 2019.